8.1 Subtidal Rocky Reefs Flashcards

1
Q

what habitat types are included in subtotal rocky reefs?

A
  • benthic rock bottoms
  • rocky slopes
  • steep rocky cliffs
  • boulder fields
  • rock slides
  • submarine caves
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2
Q

some characteristics of SRR (subtotal rocky reefs)

A
  • strong environmental gradients, e.g. light, hydrodynamics
  • strong environmental heterogeneity
  • predominantly sessile organisms
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3
Q

Kelp forest distribution

A
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4
Q

nutrients in SRR

A
  • there is seasonal fluctuations
  • the thermocline affects temperature changes but ALSO the availability of nutrient and organic matter
  • El nino events cause nutrient depletion along Californias coasts (associated with high temp. stress)
  • kelp forests at californian coasts –> extensive losses during severe events in El Niño
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5
Q

light as a gradient in SRR

A
  • vertical gradient
  • zones: photic, mesophytic, aphotic
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6
Q

gradients in SRR? vertical or horizontal?

A
  • nutrients (both: e.g. kelp forest distribution –> horizontal, fluctuations in thermocline –> vertical)
  • light (vertical+horizontal)
  • temperature (vertical+hotizontal)
  • hydrodynamism (vertical+ horizontal)
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7
Q

temperature in SRR (vertical)

A

two representative temperature profiles for the water column that is overlying wave-exposed rocky subtotal sites
(A) Gulf of Maine
(B) Galapagos Islands

(A)
- steep thermocline (between surface and13m depth)

(B)
- shallow layer of warm water (2-5m depth)
- smaller thermocline (begins at 20-23m depth)
- rocky subtotal organisms may be thermally stressed in the shallow zone (3-18m depth) when thermocline is up- and down welled

my notes:
- Upper part more variable
- Deeper areas more homogenious
- More stable environments are easier for organism –> easier to adapt (to more extreme)
- Thermocline is getting deeper and deeper in ocean (due to climate changes)
- a used-to-be stable environment but nowadays it changes
–> main factors for loss

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8
Q

hydrodynamism

A
  • vertical gradient: tides
  • horizontal gradient: currents
  • Already 14m depth are affected by wave action
  • Waves important and can be a natural disturbance

-bottom left: going from surface down: mg-calcium decreases

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9
Q

zonation in SRR

A
  • vertical zonation
  • Littoral (top)
  • Sublitoral (Infralittoral & Circalittoral)
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10
Q

picture of infralittoral kelp forest zonation

A
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11
Q

currents and hydrodynamics as horizontal gradients

A

strong horizontal gradient e.g. in caves
- caves can have particularly variable hydrodynamic conditions
- open tunnels with strong currents
- dead and caves with strong hydrodynamic confinement

  • caves also create strong light vertical gradient
  • direct effect/ influence of hydrodynamics on organisms:
    –> substrate stability
    –> availability of food and oxygen
    –> sediment deposition
    –> larval dispersion
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12
Q

zonation in caves

A
  • the zonation in caves is similar to vertical zonation
  • Less organisms in dark areas because it’s a stressed type of environment
  • Submerged sea caves are confined environments.
  • Gradients of hydrodynamics, light, food
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13
Q

Disturbances in SRR

A
  • ice scour interact with rock
  • Hurricanes in particular in tropical area and have effect on rocky shores
  • Anchoring as a disturbance from humans
  • Trawling

-the more shallow, the greater the disturbance –> the more down, the more stable

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14
Q

physical disturbances
(shallow/interdidal vs deeper water)

A

e.g. Thermal stress:
- high in intertidal and high in thermocline-zone
- Usually Thermocline: higher temp., then stabilizes at a certain point
- Now: thermocline is not stable any longer, moving more and more deeper
- If thermocline moves it’s a stressful area
- Now it’s far more unpredictable
- it is a STRESS factor here (not disturbance)
- only above dotted line is disturbance

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15
Q

where is the variability of assemblages in SRR larger?

A

larger in shallow water than in deep water assemblages

picture:
- Blue: plot looks the same, not many transitions
- Red: every time different, a lot of changes, high number of transition

surfaces have larger wave action, lots of disturbance, different temp.

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16
Q

variations in shore geometry and inclination

A
  • they have smaller scale gradients
  • overhang: usually organisms with neg. phototactic type of larval behavior, where they can be attached on upside down
17
Q

effect of different inclinations?

A
  • substrata with different inclinations show differences in species distribution
  • differences are marked
18
Q

Photofilous species

A
  • “light lovers”
  • but rather light TOLERANT
19
Q

sciophilous species

A
  • “shade lovers”
  • but rather shade TOLERANT
20
Q

microhabitat heterogeneity

A
  • Organisms create their habitat themselves (calcareous substratum is very different from the ground)
  • heterogeneity in substratum
  • heterogeneity in chemical composition
21
Q

effects of sedimentation on rocky shore assemblages

A
  • presence of sediments affect structure and functioning of rocky shore assemblages
  • sediments can naturally be present
  • sediment inputs are often altered by human activities
22
Q

sources of sediment

A
  • Discharges by rivers and river runoffs
  • Coastal Namibia because of dynomite mining
  • Comes a lot from poor human management
  • accelerated soil erosion due to clearing of forested catchments for agriculture
  • mining
  • beach nourishment
23
Q

predictability of spatial and temporal variability of sediment deposition

A
  • predictability varies
  • Sedimentation and amount of sediment is more predictable at a a larger scale
  • Differences for shore exposure:
    more predictable on shelter than exposed shores
  • it becomes less predictable as you narrow the scale
  • Sediment distribution in a very heterogeneous way –> lot of unpredictability
24
Q

how can sediment deposition be controlled?

A
  • by organisms
  • healthy canopy algae limit excess sediment deposition
  • they maintain an optimal environment for their persistence
  • if there is no canopy –> then there is lots of light –> high sediment cover (why??)
25
Q

mechanisms by which sediments affect rocky reef assemblages

A
  • burial / smothering (Verschüttung/Ersticken)
  • scour/abrasion by moving sediments (Auskolkung/Abtragung durch bewegte Sedimente)
  • changes in the physical characteristics of the
    bottom surface (even a thin layer on hard-bottom can stop recruitment of macroalgae)
  • the sediment increases turbidity and disrupts photosynthesis
  • potential interactions with organic and inorganic pollutants
  • potential indirect effects by altered bathymetry, wave and current regimes
26
Q

reported effects of sedimentation on rocky shore assemblages

A
  • effects can be variable depending on many factors:
  • Effects species-specific
  • Direct effects on individual species or their propagules and indirect effects through mediation of competitive and/or predator-prey outcomes
  • Variable effects depending on levels and composition/size of sediments
  • Variable effects depending on the scale of observation
  • Variable effects depending on other physical and biological factors (hydrodinamics, stage of development of recipient assemblages, etc)
27
Q

spatal interactions as a biotic factor influencing the distribution ,dynamics and structure of rocky shore communities

A
  • Spatial relationship are crucial in buildup of coralligenous assemblages
  • Top: A is dominant, no matter how distributed und combined
  • bottom: depending on special position A or B or C wins
28
Q

the largely overlooked role of tolerance (as a biotic factor influencing the distribution ,dynamics and structure of rocky shore communities)

A
  • When you count visually you cannot see what is underneath
  • 10% of encrusting algae means: 10% that is not covered
  • Turfs and encrusting algae can coexist
    –Extremely tolerant
    –Negatives and positives of being overgrown
29
Q

classical studies on trophic cascades (as a biotic factor influencing the distribution ,dynamics and structure of rocky shore communities)

A
  • Species from high trophic levels control the abundance and composition of species belonging to lower trophic levels (top down control)
  • The removal of sea otters caused an explosion of sea urchins with a consequent increase in the grazing of macroalgae
30
Q

predators control macroalgal vertical distribution
(kelp distribution with and without otters)

A

Vertical distribution of seaweeds
- Not only on light
- Also determined by interaction light limitation and sea urchin predation

Left graph: seaotters
- Can only dive to certain depth
- Kelps very abundant at survace bec. No urchin because seaotters eat them
- kelps controlled by light

Right: seaotters have disappeared
- Sea urchin very abundant at surface
- Kelp not controlled by light but by predation

31
Q

Trophic cascades in the Mediterranean sea

A
  • If system protected from fishery –> seaweeds come back
  • Because the urchins are controlled
  • if there are many urchins: clear water + problem of overfishing
32
Q

effect of herbivorous fish as a biotic factor influencing the distribution ,dynamics and structure of rocky shore communities

A

factor used to be largely overlooked but

  • Tropical species have a larger grazing effect
  • They come closer because of temp. rise
  • Lot of fish eat corals
33
Q

biogenic habitats - macroalgal canopies

A
  • complex morphology
  • macrolgal canopies modify the environment
  • they create habitat for many others unique assemblages of associated species
34
Q

facilitation in subtotal habitats

A
  • Urchin don’t like anemonia (similar to barnacles create obstacle for limpets)
  • Absolute reduction of grazing as function of (anemonia?)
  • Max. facilitation when a few grazers are in system
35
Q

Dispersal and Connectivity in subtotal rocky reefs

A
  • when systems are fragmented then populations might get isolated –> damage